HomeMy WebLinkAbout1990-10-30 - AGENDA REPORTS - VEHICLE AIR POLLUTION (2)AGENDA REPORT
City Manager Approval
Item to be presented
NEW BUSINESS Ken Pulskamn
DATE: October 30, 1990
SUBJECT: AB 911, Vehiclesode Sections Relating to Air Pollution
DEPARTMENT: City
BACKGROUND
Southern California's air quality is the worst in the nation, violating federal
health standards on 232 days in 1988. Ninety percent of the Southland residents
in a recent Los Angeles Times poll said they would make personal changes to
improve air quality. The percentage of air pollution is directly related to
mobile air sources, that is, largely trucks and cars. Santa Clarita Valley is
especially impacted by mobile sources since two major freeways go through this
area.
AB 911 provides that it is an infraction to operate a motor vehicle resulting in
excessive emissions of smoke, flame, gas, oil or fuel residue. It prescribes a
fine of not less than $250.00 nor -more than $2,500.00 for a first offense and
not less than $500.00 nor more than $5,000.00 for a second or subsequent offense
within one year. Revenues collected from the fines would go 25% to the
prosecuting agency, 25% to the enforcement agency, and 502 to the general fund
of the Air Quality Management District.
The Sheriffs Department has been contacted regarding AB 911 and has indicated
that they could enforce this particular section of the code at no additional
cost to the City. They could simply use the 21 officers assigned to traffic and
let them know that the enforcement of this section of the code is a high
priority for the City of Santa Clarita.
The rigorous enforcement of this particular section of the code has several
advantages: (1) first and foremost, it is a major step forward towards
improving the air quality of this region, and it gets off the road the worst
offenders of the air quality regulations; (2) it provides additional revenue for
the City of Santa Clarita; and (3) it sends a clear message to Southern
California that Santa Clarita is interested in its environment and will not
tolerate severe air polluters in its region.
It is recommended that the City Council direct the Sheriffs Department to begin
rigorous enforcement of AB 911 when it becomes a law on January 1, 1991.
Apo
,iFER Agenda item:_
.00T 15 '90 16:42
SOULI.1 Coast
AIR QUALITY MANAGEMENT DISTRICT
5150 FLAIR DRIVE, EL h40NTE. CA $1731 (818) 572.6200
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OCT 1 � 90 X16 � 4z
*• LEGI-TECH BILL TEXT R T 08127/90
'--------------------.....-----_----.-----------------------------------!
AB 911 PAGE 11
------------------------ -------------------------------------------------
1 -----
2 367 An act to amend Section 42001.2 of the Vehicle Code, relating to air
3 pollution.
4 Approved by Governor July 18, 1990
5 Filed withSecretary of State July 190 1990.
6
7 LEGISLATIVE COUNSEL'S DIGEST
8
9 AB 911, Katz. Air pollution.
10 Under existing law, it is an infraction to operate a motor vehicle in
11 a manner resulting in excessive emissions of smoke, flame, gas, oil, or
12 fuel residue. It is an infraction, subject to a fine .not exceeding
13 $1,500, to discharge, below an elevation of 4,000 feet, any air
14 contaminant which exceeds.prescribed standards, from a vehicle with a
15 gross weight rating of 6,001 or more pounds; and a violation of those
16 provisions in any otherQvehicle is an infraction punishable pursuant to
17 provisions applicable to infractions generally ($100 maximum for a•1st
18 offense, $200 maximum for a 2nd offense within one year, and $250 maximum
19 for a 3rd or subsequent offense within one year).
20 This bill would, instead of that $1,500 fine, prescribe a fine of not
21 less than $250 nor more than $2,500 for a 1st offense, and not less than
22 $500 nor more than $5,000 for a 2nd or subsequent offense within one
23 year. The bill would prescribe a fine of not less than $100nor more
24 than $250 for a 2nd or subsequent violation, in a vehicle with a gross
25 vehicle weight rating of less than 6,001 pounds, of either the provisions .
26 regarding the 4,000 feet elevation or the provisions relating
27 to excessive emissions of smoke, flame, gas, oil, or fuel residue; and
28 for the failure to correct or deliver proof of correction of either
29 violation when a notice to correct was issued and the person was
30 previously convicted of the same offense. The bill would limit the
31 penalties for a 2nd or subsequent offense to violations involving the
32 same vehicle. The bill would require the fines to be allocated to
33 designated agencies.
34
35 The people of the state of California do enact as follows:
36
37 SECTION 1. Section 42001.2 of the vehicle Code is amended.to read:
38 42001.2. (a) Every person convicted of an infraction for a violation
39 of Section 27153.5 with a motor vehicle having a manufacturer's maximum
40 gross vehicle weight rating of 6,001 or more pounds shall be punished by
41 a fine for the first offense of not less than two hundred fifty dollars
42 ($250) and not mare than two thousand five hundred dollars ($2,500), and
43 for a second or su.". equent offense. .within one year of not less than five
44 hundred dollars ($500) and not more than five thousand dollars ($5,000).
45 (b) Every perzon convicted of an infractioh'for a second or
46 subsequent violation of Section 27153, or a second or subsequent
47 violation of 27153.5, with a motor vehicle having a manufacturer's
48 maximum gross vehicle weight rating of less than 6,001 pounds, shall be
49 punished by a find of not less than one hundred dollars ($100) nor more
5o than two hundred r£ty dollars ($250).
DELETED MATERIAL T:^ IN BRACKETS [). ADDED MATERIAL IS -CAPITALIZED.
*d.****'OCT 15 '90 1643 ****k*
LETEXT RA RT 08/27/90
08127 ***F*
----..-..------------------ ---- --------------�...------
AB 911 PAGE
1 (c) Notwithst*rding Section 40616, -the penalties in subdivision (b)
2 apply when a Pers: -n is guilty of willfully violating a written promise to
3 correct, or willfully failing to deliver proof of correction, as
4 prescribed in section 40616, when an offense described in subdivision (b)
5 was the violation for which the notice to correct was issued and the
6 person was previously convicted of the same offense, except that costs of
7 repair shall be l-.nited to those specified in Section 44017 of,the Health
8 and Safety Code.
9 (d) Revenues e;511ected from fines imposed under this section shall be
10 allocated as f011nws,: 25 percent to the prosecuting agency, 25 percent
11 to the enforcement agency, except the Department.of the California
12 Highway Patrol, and 50 percent to the general fund of the air quality
13 management districor air pollution control district in which the
14 infraction occurr^.:.;. If the enforcement agency is the Department of the
15 California Highway i'atrol, the revenues shall be allocated 50 percent to
16 the prosecuting a1n;,zy,?and 50 percent to. the district in which the
17 infraction occurr.:c..
18 (e) For the pct noses of subdivisions (a), (b), and (c), a second or
19 subsequent offenac': ,.'oes not include an offense involving a different
20 motor vehicle.
BILL NO?
******OCT 15 '90 1643 ***** ***********ir** �*k***�N**�r*t***
*,LEGI-TECH COMMITTEE ;LYSIS REPORT 10/15/90
------------------------------------------------------------------•-------
AB 911 06/19/90 SENATE COMMITTEE ON TRANSPORTATION PAG$ 1
SENATE TRANSPORTATION COMMITTEE
BILL NO.: AB 911
AUTHOR: KATZ
VERSION: (Orig.)
Amended 08/11/90
FISCAL: NO
SUBJECT:
Air pollution.
DESCRIPTION:.
This measure would revise the fine schedule for violation of emission
standards.
ANALYSIS:
Under existing law, it is an infraction to operate a motor vehicle in a
manner resulting in excessive emissions of smoke, flame, gas, oil or fuel
residue. The fine for excessive discharge below an elevation of 4,000 feet
from a vehicle with a gross weight rating of 6,001 or more pounds may not
exceed $1,500. There is no prescribed minimum. For any other vehicle the
fine is that which is applicable to infraction in general ($100 maximum
for a first offense, $200 maximum for a second offense within one '.year,
and $250 maximum for a third or subsequent offense within one year).
This bill would, instead of that $1,500 fine, prescribe a fine of not less
than $250 nor more than $2,500 for a first offense, and not less than $500
nor more than $5,000 for a second or subsequent offense within one.year.
The bill would prescribe a fine of not less than $50 nor more than $250
for a second or subsequent violation, in a vehicle with a gross vehicle
weight rating of less than 6,001 pounds, or either the provisions
regarding. the 4,000 feet elevation or the provisions relating to excessive
emissions of smoke, flame, gas, oil or fuel residue; and for the failure
to correct or deliver.proof of correction of either violation when a
notice to correct was issued and the person was previously convictedlbf
the same offense.
Revenues collected from fines imposed under this bill must be allocated as
follows: 25 percent to the prosecuting agency, 25 percent to the
enforcement agency, except the Department Of the California Highway
Patrol, and 50 percent to the general fund•of the air quality management
district or air pollution control district in which the infraction
occurred. If the enforcement agency is the Department of the California
Highway Patrol, the revenues must be allocated 50 percent to the
prosecuting agency, and 50 percent to the district in which the infraction'
occurred.
COMMENTS:
This bill, as it passed the Assembly, was authored by Assembly Member
Killea and dealt with low emission vehicles. The text and the author are
new to this bill.
POSITIONS: (Communicated to the committee before noon on
Thursday, June 14, 1990).
SUPPORT: South Coast Air Quality Management District
Bay Area Air Quality Management District
County of Tehama Air Pollution Control District
SILL NO?
16:44 • � P.SiB
11. MCKGROUND ON DIESEL ENGINES LAND THEIR EMISSIONS
3`;,,.• Since the.developnient of the first Diesel -cycle engine about
90 years ago, it has become a power source for both motor vehicle
and stationary (e.g., industrial). applications. The appeal of the
Diesel -cycle engine is its ability to provide high efficiency over
a wide range of loads and speeds while using simple, distillate
fuel. Although not an inherent feature of the combustion process,
most of the Diesel engines that have been developed for heavy-duty
vehicles provide much greater durability.than is associated with
gasoline engines. As a result, Diesel engines.are a popular
powerplant for trucks and buses throughout the world.
While much progress has been made to control Diesel
emissions, further reductions still need to be made. By 1990, it
is estimated that 200,000 heavy-duty Diesel -powered vehicles will
be in service statewide and they will tally 27 million miles per
day•and consume 1.5 billion gallons of Diesel fuel per year.
rhese Diesel vehicles contribute significantly to the overall air
pollution problem, and in a tampered or malmaintained state are an
especially visible source of smoke and -soot.
The pollutants emitted by Diesel vehicles include unburned
:hydrocarbons (HC), carbon monoxide (CO), oxides of sulfur (Sox),
,.oxides of nitrogen (Nox), particulate matter (PH), and other
,,potentially toxic compounds. Diesel vehicles emit relatively low
i1svels of HC and CO,.and relatively high levels of NOx and PM
.compared to gasoline vehicles. It should be noted that even
;:though Diesel vehicles emit relatively low levels of HC and CO,
these emissions will represent an increasing portion of the
"remission inventory in years to come as other.HC and CO sources are
ther controlled. To limit the.emission of pollutants by Diesel
vehicles, the ARB has enacted stringent standards affecting such
emissions. A summary of these standards is presented in Table 5.
The following paragraphs provide a brief description of.the
::health concerns posed by the pollutants emitted by Diesel engines,
':followed by an inventory of the Diesel emissions from stationary
and -mobile sources. A more extensive discussion of the health and
:environmental problems associated with exposure to Diesel
remissions can be found in Appendix B.
>'<:+ HC emissions pose two health concerns. HC emissions by
;'themselves can be comprised of toxic and suspected toxic
compounds. Once the HC emissions enter the ambient air they
combine with other compounds to form ozone in the photochemical
..smog process.
acs,..., ,... ...
-13-
'90 16:45
• 0
Table 5
Emission
Standards
for Diesel Vehicles
g/mi -------------
Fox
*
-------------
g/mi--------------
10,6
Passenger Cars
HC
CO NOx
PM
10.6
• 1.0
0.40
1986
1982
0.46
8.3 1.5
0.60
1985 .
0.46
8.3 1.0
0.40
1986
0.46
8.3 1.0
0.20
1989
0.46
8.3 1.0
0.08
*
Light Trucks:
.............
HC
CO
g/mi -------------
Fox
PM
1982
0.46
10,6
1.5
0.60
1985
0,46
10.6
• 1.0
0.40
1986
0.46
10.6
1.0
0.20
1989
0.46
10.6
1.0
0.08
Heavy -Duty Trucks
........... g/bhp_hr ---------=--
and Buses:
HC
CO
NOx
PM
1988
(ail)
1.3
15.5
6.0
0.60
1991
(truck)
1.3
15.5
5.0
0.25
1991
(urban buses)
1.3
15.5
5.0
0.10
1994
(truck)
1.3
15.5
5.0
0.10
*100,000 mile certification distance required.
P.6/8
,;:.r Human exposure to CO -emissions can cause angina, dizziness
and fatigue, and can impair control of nervous system functions.
Ambient CO concentrations in.certain areas oftheSouth Coast Air
Basin, for example, are about two times the federal and state
health -based standards. In 1985, unhealthy levels of CO occurred
on more days in the South Coast Air Basin than in any other area
in'the country except New York City.
Another pollutant emitted from Diesel engines is 50x. Sox
emissions are primarily composed of sulfur dioxide (SO2) and
sulfur trioxide 009). Both pollutants pose health and
environmental concerns. SO, is of.special concern because it
reacts rapidly with water vapor in the exhaust stream or in the
.atmosphere to"form sulfuric acid. SO2 also contributes'to the
formation of sulfuric acid, the formation of sulfate aerosols
which are a form of particulate matter, and the formation of acid
rain. Exposure'to SOx emissions adversely affects the human
respiratory system. Symptoms are shortness of breath, increased
respiratory tract infections, and chronic bronchitis.
One of the pollutants that is of special concern is NOx
because Diesel engines are not compatible with catalytic NOx
-14-
16:46 • � P. 7/8
1
a?:.control, as are gasoline -powered engines. Nitric oxide (NO)
accounts for most -of the NOx emissions from Diesel engines. By
itself, NO does not pose a health concern. However, in the
atmosphere NO is quickly oxidized into nitrogen dioxide (NO2)
.; which poses both a health and environmental concern. Exposure -to
=: NOs decreases lung function and may reduce resistance to
infection. Although the federal ambient NOs standard. of 0.053 ppm
-,.was exceeded in the South Coast Air Basin by only 2 percent in
1987, the more important state 1 -hour average air quality standard
(0.25 ppm) was exceeded by 688. NO: in the atmosphere is also. a
precursor to ozone formed through the photochemical smog process.
Diesel NOx emissions are generally difficult to control
,.;:'because NOx-specific.control techniques often tend to increase
other emissions and also increase fuel consumption. The NOx
controls for Diesels include combustion chamber design changes,
Ignition timing r%tard and exhaust gas recirculation (ECR). The
NOx reduction catalyst used on gasoline engines cannot be adapted
because Diesel engines operate with excess air while NOx catalysts
require the chemically ideal amount of air, or insufficient air.
Another pollutant of -concern is particulate matter (PM). PM
can either be directly emitted into the atmosphere as a -by-product
Of fuel combustion, or can be emitted through abrasion, typically
from tire -wear or brake linings. The major source of motor
vehicle PM emissions is from tire -wear. Tire -wear PM is not a
major health concern because these emissions tend to be greater
than 10 microns in diameter. These larger particles cannot
penetrate deep into the lungs.
Diesel exhaust PM, on the other hand, is less than 10 microns
in diameter (PM10) and poses a serious health risk. The small
size of -Diesel PM10 allows the particle to be drawn deep into.the
lungs where the result can be serious respiratory ailments.
Almost all of the motor vehicle PM10 emissions are emitted from
Diesel -powered vehicles. Health effects resulting from exposure
to PM1O include cell damage to the lung tissue, narrowing of the
air passages within the lungs, and reduced pulmonary function. In
addition, the particles carry carcinogenic and other toxic
compounds which adhere to the particles. Breathing these
particles causes ad increased risk of cancer.
.;; Although ozone is not directly emitted from Diesel engines,
if is formed through photochemical conversion of NOx and HC
emissions which are emitted from Diesel engines. Ozone is a
1,1::.strop oxidant
g and poses a significant risk to public health.
Studies have shown that exposure to elevated ozone concentrations
results in reduced lung function, particularly during vigorous
Physical activity. This health problem is particularly acute in.,
children, the elderly, and those with impaired lung function.
Besides the previously mentioned pollutants, Diesel engines
emit a variety of other compounds. These emissions include
aldehydes; benzene; 1,3 butadiene; polynuclear aromatic
-15-
'90 16:4716
64716 P. 8/6
hydrocarbons (PAM); and xylene. Some of these compounds are known
or suspected carcinogens and are under investigation as possible
Toxic Air Contaminants (TAC's).
Diesel engines are used in mobile (vehicular) and stationary
applications. Stationary Diesel engines are generally larger
an than those used for vehicles. These engines usually
operate at lower engine speeds (360 to 1200 rpm) and at a constant
speed. Stattonary engines are typically used for electric power
generation, and for the pumping of water, oil or sewage.
The emissions from Diesel mobile sources -are classified as
either on-road-or'as "other" mobile sources. On -road Diesel
sources include four major categories, or.classes of motor
vehicles: light-duty passenger cars, light-duty trucks, medium -
duty trucks, and heavy-duty trucks. The "other" mobile sources
.encompass a wide :variety of vehicles and include farm, •
construction, utility, marine, and locomotive engines. All of the
•other" sources are currently unregulated, but studies to assess
the feasibility of reducing emissions are in progress and could
lead to the adoption of emission.standards within 2 to 5 years.
The estimated statewide emissions from Diesel sources are
presented in Table 6.
Table 6
Estimated
Statewide
Emissions
of SO2,
NOXI PM10
From Diesel -Powered
Sources
(Tons Per Day in 1990)
........
.... Pollutant
..................
.......-..
PM10 -----------
Source Category
S02
NOx
Fugitiv0 0ther2
Total
Total
487
2824
2822
485 ..
3307
Stationary
262
889
2760
339
3099
Mobile
225
1935
62
146
208
On -Road Mobile 80 517 76 9 85
Other Mobiles 145 1418 70 53 123
r Fugitive PM10 includes all emissions that are considered
uncontrollable.such as road dust, agricultural tillage dust, tire
wear, and brake lining wear, etc.
2 "Other'!PM10 emissions consist of PM10 emissions other than road
.dust, windblown dust; agricultural tillage dust, etc.
? Other mobile sources include trains, off-road construction equipment,
and utility equipment, etc.
Source: ARB/SSD/TSD
.16-
Motion:
That the City Council issue a declaration of'policy regarding .
the potential acquisition of title to the Saugus Rehabilitation
Center as follows:
The Cit of Santa Clarita IS interested in acquiring
cF ?n �p �e a ttan
Y.he S��gus Rehabilitation Center
•AuyeJEaa for park and recreation purposes and for other
municipal purposes.
2. The City of Santa.Clarita is NOT interested in
acquiring title to the Saugus Rehabilitation Center from the
City of Los Angeles pursuant to and subject to the terms and
conditions of the Joint Exercise of Powers Agreement creating'.
the Los Angeles Solid Waste Authority.
d